Local metabolism in lung airways increases the uncertainty of pyrene as a biomarker of polycyclic aromatic hydrocarbon exposure

While inhaled polycyclic aromatic hydrocarbons have long been suspected to induce lung cancer in humans, their dosimetry has not been fully elucidated. A key question is whether the critical exposure occurs during absorption in the lungs, or if toxicants in the systemic circulation contribute significantly to lung cancer risk. In particular, data are needed to determine how the physical properties of inhalants affect local dosimetry in the respiratory tract. Pyrene, a tobacco smoke component, was selected for study because it has physical properties between those of highly lipophilic benzo[a]pyrene and water-soluble nitrosamines. Aliquots of 5 ng of pyrene dissolved in a phospholipid/ saline suspension were instilled as a single-spray bolus in the posterior trachea of the dog just anterior to the carina. For 3 h after instillation, blood was repeatedly sampled from the azygous vein, which drains the mucosa around the point of instillation, and from both sides of the systemic circulation. At 3 h post-instillation, tissue samples were taken. Autoradiography was used to determine the depth distribution of pyrene in the tracheal mucosa. The concentration of pyrene-equivalent radioactivity in the azygous vein peaked 9 min after the instillation. At approximately 30 min after instillation, a rapid early clearance phase shifted into a distinctly slower second clearance phase. Rates of rapid clearance were, however, sufficiently slow to indicate diffusion-limited absorption of pyrene in the trachea. This finding was corroborated by high concentrations of pyrene in the epithelium as determined by autoradiography. High epithelial concentration of pyrene combined with a slow penetration into the circulating blood allowed substantial first-pass metabolic conversion of pyrene in the tracheal mucosa. A total of 13% of the instilled pyrene was retained in the tracheal mucosa 3.2 h after instillation; of this, 29% was parent compound, 52% was organic-extractable metabolites, 14% was water-soluble metabolites and 6% (approximately 1% of the instilled amount) was covalently bound to tracheal tissues. Results support the inference that lipophilic protoxicants, because of slow, diffusion-limited absorption, are more likely than water-soluble protoxicants to be bioactivated in the lining epithelium and, in turn, induce first-pass toxicity at the site of entry. In addition, limitations were identified in the use of systemically distributed biomarkers of PAHs, such as urinary hydroxypyrene levels, as indicators of the biologically effective dose in airway target cells.

The effect of diesel exhaust particles on cell function and release of inflammatory mediators from human bronchial epithelial cells in vitro

Animal studies have reported that diesel exhaust particles (DEP), which constitute an important fraction of particulate air pollution, lead to inflammation and/or damage of the airways. To investigate the mechanisms underlying DEP-induced airway disease in humans, we have cultured human bronchial epithelial cells (HBEC) from surgically obtained bronchial explants and investigated the effects of purified DEP on the permeability and ciliary beat frequency (CBF) of HBEC, and on the release of inflammatory mediators from these cells. Exposure to 10-100 microg/ml DEP and a filtered solution of 50 microg/ml DEP significantly increased the electrical resistance of the cultures, reaching a maximum of 200% over baseline after 6 h incubation with 100 microg/ml DEP. In contrast, movement of 14C-labeled bovine serum albumin across cell cultures was not significantly altered by incubation of HBEC with DEP. Exposure to 50 microg/ml DEP, filtered DEP solution, and 100 migrog/ml DEP significantly attenuated the CBF of these cells by 51%, 33%, and 73%, respectively, from baseline after 24 h incubation. Similarly, 50 microg/ml DEP, filtered DEP solution, and 100 microg/ml DEP significantly increased the release of interleukin-8 from 12.9 pg/microg cellular protein to 41.6, 114.9, and 44.3 pg/microg cellular protein, respectively, after 24 h incubation. The release of granulocyte-macrophage colony stimulating factor (GM-CSF) and soluble intercellular adhesion molecule-1 (sICAM-1) was also significantly increased after exposure for 24 h to 50 microg/ml DEP (GM-CSF from 0.033 pg/microg cellular protein to 0.056 pg/mug cellular protein and sICAM-1 from 7.2 pg/microg cellular protein to 12.5 pg/microg cellular protein). These results suggest that exposure of HBEC to DEP may lead to adverse functional changes and release of proinflammatory mediators from these cells, and that these effects may influence the development of airway disease.

A comparison of the tumors induced by coal tar and benzo[a]pyrene in a 2-year bioassay

The tumorigenicity of two coal tar mixtures was compared to that of benzo[a]pyrene after 2 years of feeding. Mixture 1, a composite of coal tar from seven coal gasification plant waste sites, was fed to female B6C3F1 mice (48 mice per group) for 2 years at doses of 0.0, 0.01, 0.03, 0.1, 0.3, 0.6 and 1.0%. Mixture 2, which was composed of coal tar from two of the seven waste sites and another site having a high benzo[a]pyrene content, was fed at doses of 0.0, 0.03, 0.1 and 0.3%. Additional groups of mice were fed 0, 5, 25 and 100 ppm benzo[a]pyrene. The coal tar diets induced a dose-related increase in hepatocellular adenomas and carcinomas, alveolar/bronchiolar adenomas and carcinomas, forestomach squamous epithelial papillomas and carcinomas, small intestine adenocarcinomas, histiocytic sarcomas, hemangiosarcomas in multiple organs and sarcomas. Benzo[a]pyrene treatment resulted in an increased incidence of papillomas and/or carcinomas of the forestomach, esophagus and tongue. A comparison of the results indicated that the benzo[a]pyrene in the coal tar diets could be responsible for the forestomach tumors. In contrast, the lung and liver tumors appeared to be due to other genotoxic components contained within the coal tar mixture, while the small intestine tumors resulted from chemically-induced cell proliferation that occurred at high doses of coal tar.

Comparison of the mutational specificity induced by environmental genotoxin nitrated polycyclic aromatic hydrocarbons in Salmonella typhimurium his genes

Mutagenicity of 15 nitrated polycyclic aromatic hydrocarbons (nitro PAHs), which were detected in ambient air particles and/or combustion source emissions, were examined using a set of six Salmonella typhimurium tester strains (TA7001 to TA7006), and the mutational specificity was characterized by the comparison of the mutagenic potencies of nitro-PAHs in the tester strains. Each strain carries a unique missense mutation in the histidine operon and is reverted by only one specific base-substitution out of six possible changes. All nitro-PAHs tested were mutagenic in multiple strains, and were classified into four categories based on the strains predominantly reverted. 1-Nitropyrene (1-NPy), 2,7-dinitrofluoren-9-one and 1,3-, 1,6- and 1,8-dinitropyrene isomers exerted the highest mutagenicity in strain TA7005 (C.G-->A.T transversion) followed by strain TA7006 (C.G-->G.C transversion). 2- And 3-nitrofluoren-9-one isomers, 2-NPy and 2,7-dinitrophenanthrene were also markedly mutagenic in strain TA7005 but not in strain TA7006. For 2-, 3- and 9-nitrophenanthrene isomers, 2-nitrofluoranthene (2-NFT) and 4-NPy, TA7004 (G.C-->A.T transition) was the most responsive strain. 3-NFT was unique, showing the highest mutagenicity in strain TA7002 (T.A-->A.T transversion). All nitro-PAHs tested induced C.G-->A.T transversion, which is observed as the most frequent base-substitution mutation of p53 tumor suppressor gene in human lung cancer.

Possible relevance of pigeons as an indicator species for monitoring air pollution

Wild city pigeons were caught at four different locations in the Netherlands to represent areas of high (Amsterdam-high), moderate (Amsterdam-medium), and low (Maastricht and Assen) traffic density. It is assumed that local ambient air pollution decreases as a function of traffic density. In these pigeons levels of polycyclic aromatic hydrocarbon (PAH)-DNA adducts, oxidative DNA damage, and heavy metal residues were determined in kidney, lung, liver, and blood (no adduct analysis in blood). The contribution of leaded gasoline to total body lead content was estimated by measuring concentrations of Pb and its isotopes in blood. We also analyzed samples of ambient air particulate matter for PAH and heavy metal concentrations at the four different locations. Interregional differences in heavy metals in ambient air particulate matter were reflected relatively well by pigeon body loads. The higher lead and cadmium concentrations in blood, kidney, liver, and lung were found in the Amsterdam high traffic density area, followed by Amsterdam medium, Assen, and Maastricht. A high Pb concentration in blood coincided with relatively low 206Pb/207Pb values, indicating a high contribution of leaded gasoline to total blood Pb concentrations in pigeons from the Amsterdam high traffic density area. Significantly enhanced blood zinc values were found in pigeons from both locations in Amsterdam compared to pigeons from the other two areas. However, no differences in Zn tissue levels between the four different groups were found. Oxidative DNA damage, determined as the ratio of 7-Hydro-8-oxo-2'-deoxyguanosine/ deoxyguanosine, in pigeon liver was highest in Amsterdam-high, followed by Assen (low traffic density). Pb content, but not the Cd content, was positively associated with oxidative DNA damage in liver tissue. In lung tissue, a negative correlation was found between oxidative DNA damage and Zn content. These results indicate that the carcinogenic potential of Pb might be ascribed to oxygen radical formation, whereas Zn plays a protective role against oxidative DNA damage. Places with high and medium traffic density could be clearly discriminated on the basis of PAH levels in the ambient air. The PAH content in particulate air samples was not, however, reflected in total PAH-related DNA adduct levels because no differences could be observed in tissue adduct levels in pigeons from the four different locations. Our results indicate that wild city pigeons can be used as biological indicators of exposure to heavy metal pollution in outdoor air.

Relationship between resonance energy and carcinogenicity of azaarenes

Resonance energy per pi-electron (REPE) of azaarenes were calculated by Aihara's theory of resonance energy (TRE). Consequently, it was shown that the REPE values for the cationic species not having the carbon, or nitrogen atom with the highest approximate superdelocalizability (Sr'(E)) in the parent skeleton were more unstable than those of their parent skeleton. Some correlations seem to exist between the REPE values for the cationic species not having the atom with the highest value of (Sr'(E)) in parent skeleton and carcinogenic activity. Other types of correlations can be assumed in the case of carbazoles 7H-benzo[g]pyrido[2,3-a]carbazole (14), 13H-dibenzo[a]pyrido[3,2-i]carbazole (17), and 7H-benzo[c]pyrido[2,3-g]carbazole (20) although there are some exceptions, i.e., 7H-benzo[g]pyrido[3,2-a]carbazole (15) and 7H-dibenzo[c,g]-carbazole (18). The bond-order affected carcinogenicity induction in some ways as well.

Systemic and developmental toxicity of dermally applied syntower bottoms in rats

Syntower bottoms (STB) was evaluated for subchronic and developmental toxicity. In the subchronic study, undiluted STB was applied on the shaved backs of male and female rats at dose levels of 0, 8, 30, 125, and 500 mg/kg for 13 weeks, 5 days per week. Exposure sites were not covered. In the developmental toxicity study, STB was similarly applied, but to pregnant rats at dose levels of 0, 8, 30, and 125 mg/kg on Gestation Days 0-19. In addition, 4 mg/kg was dosed as 8 mg/kg every other day, starting on Gestation Day 0, and 500 mg/kg was dosed on Gestation Days 10-12. Evidence of toxicity observed in the subchronic study included death, decreased body weights, aberrant serum chemistry and hematology values, altered organ weights, and histopathologic changes in a variety of organs. A no observed adverse effect level for systemic toxicity could not be established. Evidence of maternal toxicity was observed at all exposure levels in the development study. Regardless of the length of the exposure period, STB was toxic to the developing conceptus. Evidence of developmental toxicity observed included increased resorptions with a concomitant decrease in litter size and reduced fetal body weights. Cleft palate was observed in fetuses exposed in utero to STB during Gestation Days 10-12 at 500 mg/kg. No evidence of teratogenicity was observed when the exposure period was throughout gestation. Ossification delays were observed in fetuses exposed in utero to STB at doses in excess of 4 mg/kg. A no observed adverse effect level for maternal and developmental toxicity could not be established.

Direct mutagenicity of the polycylic aromatic hydrocarbon-containing fraction of smoked and charcoal-broiled foods treated with nitrite in acid solution

The polycyclic aromatic hydrocarbons (PAH) containing fractions of smoked and charcoal-broiled foods, namely, Sheat fish (Kytopterus apogon), Mimrow (Crossocheilus reba), Freshwater catfish (Clarias batrachus), chicken wings, rice pork sausage and pork, in addition to naphthalene, acenaphthene, anthracene, phenanthrene, fluoranthene, pyrene, benz[a]anthracene, naphthacene, benzo[a]pyrene, benzo[e]pyrene, 9,10-dimethyl-1,2-benzanthracene, dibenz[ah]anthracene, benzo[ghi]perylene and coronene, were evaluated for their mutagenic potential using Salmonella typhimurium strains TA98 and TA100 in the absence of metabolic activation after being treated with nitrite (500 mM) for 4 hr at 37 degrees C and in acid solution pH 3.0-3.5. The presence of N-nitroso compounds was also determined. Results showed that nitrite could convert most samples to direct-acting mutagens towards both strains except for fluoranthene and benzo[ghi]perylene, which exhibit mutagenicity only with TA98. It was demonstrated that treatment of PAHs with nitrite in acid solution produced some non-N-nitroso direct-acting mutagens, suggesting that they might belong to nitro-PAHs. Therefore, the consumption of charcoal-broiled and smoked foods simultaneously with nitrite is not recommended.

Nitroarenes of photochemical origin: a possible source of risk to human health

Nitrated polynuclear aromatics (NPAH) have been recognized as mutagenic even without enzymatic activation. NPAH have been found in the urban air of the U.S.A. and Western Europe. Their detection in the atmosphere has been related mainly to in situ photochemical production. In this study, the ubiquity of NPAH in the air is presented despite their rare and scarce occurrence in emissions released by mobile and stationary sources. NPAH seem to effectively contribute to both the direct and indirect mutagenicity of air soot (in European countries more than in the U.S.A.). Moreover, they can be taken as a suitable index of the occurrence of reactive nitrogen compounds in the air.

[Genotoxicity of urban air particulate matter]

This paper reviews the genetic toxicology of urban air particulate. Dusts present in the urban environment are composed of a special type of soot, currently mainly emitted by motor vehicles. This soot contains variable quantities of adsorbed highly active genotoxic compounds (polycyclic aromatic hydrocarbons and their nitro derivatives, i.e., nitroarenes). Nitroarenes are among the compounds with the highest genotoxic activity according to the Ames test (genetic point mutation on bacteria), and are particularly abundant in ultrafine particulate matter (< 1.1 microns) emitted by diesel engines, mainly trucks. Diesel emissions have been considered as probable carcinogenic agents for man by the International Agency for Research on Cancer (IARC). Highly mutagenic activity is present in the air of all the cities in the world, and there is increasing concern about possible carcinogenic effects on the general population as a result of exposure to urban particulate matter. Early epidemiological studies on city-dwellers exposed to heavy pollution indicate an excess of lung tumours. Lastly, there is a possible carcinogenic risk for occupationally exposed workers, such as traffic police and those working for city road cleaning services, etc., who are constantly obliged by their jobs to be exposed to polluted city air at work.

Risk assessment of complex mixtures: some considerations on polycyclic aromatic hydrocarbons in urban areas

The comparative examination of experimental and epidemiological data, together with risk evaluations concerning coke-oven, diesel, and gasoline motor emissions, as well as specific PAH fractions and single PAHs, indicates that, at least under risk additivity hypothesis, benzo(a)pyrene (B(a) may account for only a relatively small amount of the whole carcinogenic potential of PAH mixtures. This finding emerges from the comparison of risk evaluations of coke-oven and diesel emissions (based on epidemiological and/or experimental data) with risk evaluations of B(a)P as a single substance (based on carcinogenic bioassay data), as well as from the results of experimental studies evaluating the carcinogenic potency of motor exhaust condensates, of specific condensate fractions (particularly, the 4-7 ring PAH fraction), and of B(a)P. These data indicate that B(a)P might account for a percentage of the whole mixture carcinogenic response, at least in the hypothesis of an additive effect of PAHs. However, the overall carcinogenic response and risk still appear at least approximately related to the B(a)P concentration in the examined PAH mixtures. Finally, recent findings on PAH relative potencies (compared with B(a)P potency) indicate that several PAH present in mixtures commonly detected in occupational and in the general environment are characterized by a carcinogenic potency comparable with or even higher than that of B(a)P. This confirms the above hypothesis with respect to the significant, but minor role, of B(a)P. This relatively coherent picture appears to confirm that the reference to B(a)P as a complex mixture index may still represent a reasonable solution. However, the selection of a few other indicators from among the PAH whose relative concentrations and relative carcinogenic potencies are higher might improve the analysis.

Health risk assessment of an industrial site contaminated with polycyclic aromatic hydrocarbons using CalTOX, an environmental fate/exposure model

This paper presents the results of a risk assessment study made using CalTOX, a multimedia, multiple pathway risk assessment model. The case study is based on the Polycyclic Aromatic Hydrocarbon (PAH) soil contamination resulting from the activities of a natural gas power station over a period of 70 years. It describes model characteristics and input parameters such as physico-chemical properties, landscape description, and human exposure factors. Model simulations and risk estimations corresponding to different remedial scenarios in an industrial zone are also presented. These estimations were based on soil contamination by 16 PAHs in the root-zone and vadose-zone layer. Results show that adult exposure (workers) to contaminated soil will lead to a potential health risk of carcinogenic effects, and to no potential risk of non-carcinogenic effects. On the other hand, the addition of 10 cm of clean soil over the contaminated soil (mitigated scenario) decreases the lifetime cancer risk to an acceptable level. The sensitivity analysis showed that the half-life of benzo[a]pyrene in the root-zone soil is the most sensitive parameter and that it contributes significantly to the variability of the cancer risk estimation. In addition, the cancer risk level of the workers exposed to this substance, as estimated by CalTOX (point estimate) in the mitigated and unmitigated scenario, corresponds approximately to the 95th percentile value obtained by means of Monte-Carlo simulations. Finally, CalTOX has proven to be a valuable tool to predict and elaborate scenarios for the risk management of sites contaminated as a result of industrial activities.

[Organ cytotoxicity of selected polycyclic aromatic hydrocarbons in mice]

The cytotoxic effects of some PAHs: DMBA, 3-MC and B(a)P on the lymphatic organs, liver and kidney of mice have been investigated. These PAHs in doses of 100 mg/kg were dissolved in 0.5 ml 20% DMSO and were given intraperitoneally in female mice Balb/c. After 7 days, organs weight, cellularity in lymphoid organs and tissue structure of liver and kidney were analyzed. The greatest effect of DMBA was observed on cellularity of spleen. 3-MC and B(a)P caused significant hepatotoxic and nephrotoxic changes. 3-MC induced focal destruction of hepatocytes and sometimes--irregular mitotic figures (c-mitosis). After B(a)P administration in liver cells were mainly observed the changes in distribution of interphase nucleolar organizer region (AgNOR). In kidney--irregular glomeruli and tubuli after 3-MC and B(a)P were noted. The above results may indicate that the cytotoxic effects of PAHs depend on the type of compound administered.

Airborne levels of polycyclic aromatic hydrocarbons: 32P-postlabeling DNA adducts and micronuclei in white blood cells from traffic police workers and urban residents

An epidemiologic study on 94 traffic police officers exposed to airborne polycyclic aromatic hydrocarbons (PAH) and 52 age-matched urban residents working in confined spaces considered as referent subjects without occupational exposure to PAH was conducted to characterize individual exposure to benzo(a)pyrene (BaP), benzo(b)-, and benzo(k)fluoranthene (BbF and BkF) and the occurrence of DNA adducts and micronuclei in white blood cells (WBC). The study's findings indicated that mean concentrations of PAH in the city air were 10 to 30 times higher among the traffic police officers compared with referent subjects (4.55 +/- 3.44 ng/m3 and 0.15 +/- 0.30 ng/m3 of BaP among police officers and referents, respectively). 32P-postlabeling DNA adducts in WBC obtained from police officers (1.48 +/- 1.35 RAL/10(8)) were significantly higher than in referent subjects (1.01 +/- 0.63 RAL/10(8), P = 0.007), suggesting a possible role of exposure to airborne PAH in the DNA damage. The frequency of micronuclei was significantly increased (P = 0.02) in referent subjects (4.49 +/- 2.0% cells) compared with police officers (3.75 +/- 1.65% cells) due to the large proportion of females in the former group. Comparison of the mean micronuclei frequencies among 82 male police officers (3.73 +/- 1.6% cells) and referents (4.03 +/- 1.61% cells) failed to reveal a statistically significant difference (P = 0.38). Our findings support the evidence of a noxious effect of the exposure to airborne PAH found in large cities on the occurrence of DNA adducts in WBC, whereas there seems to be no effect on the cytogenetic risk assessed as micronuclei frequency.

Chemical analysis and biological activity of airborne particulate matter

We examined the chemical composition of the suspended particulate matter in a typical, middle-sized, nonindustrial Italian town in terms of total carcinogenic PAH, heavy metal, and polynuclear azo-aromatic compounds. The chemical data relate to the biological activity of the organic extract of the particulate matter (mutagenicity and mice alveolar macrophage phagocytosis inhibition). The concentration values of benz(a)pyrene, the concentration ratios of selected PAH's, and the GC-MS profile of some typical samples indicate that motor vehicle traffic is the main pollution source. PAH concentration is significantly correlated with mutagenicity and a phagocytosis inhibition of up to 75% was observed at the highest PAH concentration. As far as the effect of meteorological variables on PAH concentration and mutagen-icity is concerned, a statistically significant inverse correlation with temperature was found.

Human cell mutagenicity of oxygenated, nitrated and unsubstituted polycyclic aromatic hydrocarbons associated with urban aerosols

Polycyclic aromatic compounds (PAC) are ubiquitous pollutants in urban air that may pose risks to human health. In order to better assess the health risks associated with this class of compounds, a total of 67 PAC that either have been identified (55) or are suspected to be present (12) in urban aerosol samples were tested for mutagenicity in a forward mutation assay based on human B-lymphoblastoid cells. The cell line used (designated h1A1v2) constitutively expresses the cytochrome P4501A1, which is known to be necessary for the metabolism of many promutagens. The PAC tested included 39 polycyclic aromatic hydrocarbons (PAH). 19 oxygen-containing PAH (oxy-PAH) and nine NO2-substituted PAH (nitro-PAH). A total of 26 PAH were mutagenic. In comparing the minimum mutagenic concentrations of the mutagenic PAH with that of benzo[a]pyrene (B[a]P) it was found that dibenzo[a,l]pyrene (DB[al]P), cyclopenta[c,d]pyrene (CPP), naphtho[2,1-a]pyrene, dibenzo[a,e]pyrene (B[a]P) and 1-methylbenzo[a]pyrene were 24 +/- 21, 6.9 +/- 4.2, 3.2 + 3.0, 2.9 +/- 2.9 and 1.6+/- 1.4 times, respectively, more mutagenic than B[a]P, and that dibenzo[a,k]fluoranthene and B[a]P were approximately equally mutagenic. The 19 other mutagenic PAH were between approximately 2 and approximately 1800 times less mutagenic than B[a]P. Of the oxy-PAH tested only phenalenone, 7H-benz[d,e]anthracen-7-one, 3-nitro-6H-dibenzo[b,d]pyran-6-one, cyclopenta[c,d]pyren-3(4H)-one, 6H-benzo[c,d]pyren-6-one (BPK) and anthanthrenequinone were mutagenic; however, with the exception of BPK, these were over 50 times less active than B[a]P, BPK was approximately 3 times less active than B[a]P. Seven of the nitro-PAH were mutagenic including 9-nitroanthracene, 1-nitropyrene, 2-nitrofluoranthene, 3-nitrofluoranthene, 1,3-dinitropyrene, 1,6-dinitropyrene (1,6-DNP) and 1,8-dinitropyrene. 1,6-DNP was approximately 4 times less active than B[a]P; the six other mutagenic nitro-PAH were between 20 and 380 times less active than B[a]P. These results are discussed in terms of their relevance for determining the most important mutagens in ambient air. Based on reported concentrations of PAC in ambient aerosols, it is possible that CPP, DB[ae]P, DB[al]P and BPK could account for a greater proportion of the mutagenicity than B[a]P in some aerosols.

Cytochrome P4501A induction in avian hepatocyte cultures: a promising approach for predicting the sensitivity of avian species to toxic effects of halogenated aromatic hydrocarbons

Concentration-dependent effects of halogenated aromatic hydrocarbons (HAHs) on cytochrome P4501A (CYP1A) induction in primary hepatocyte cultures prepared from embryos of chickens (four breeds), pheasants, turkeys, ducks (three breeds), and herring gulls were determined. CYP1A activity was estimated by measuring ethoxyresorufin O-deethylase (EROD) activity and the concentration of immunodetectable CYP1A was estimated using mouse monoclonal antibody 1-12-3 that was prepared against scup (Stenotomus chrysops) CYP1A1. The HAHs studies were 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), 2,3,7,8-tetrachlorodibenzofuran (TCDF), 3,3',4,4'-tetrachlorobiphenyl (PCB 77, IUPAC nomenclature), 3,4,4',5-tetrachlorobiphenyl (PCB 81), 3,3',4,4',5-pentachlorobiphenyl (PCB 126), 3,3',4,4',5,5'-hexachlorobiphenyl (PCB 169), 2,3,3',4,4'-pentachlorobiphenyl (PCB 105), and 2,3',4,4',5-pentachlorobiphenyl (PCB 118). Two general types of comparisons were made: (1) relative potencies of compounds within a species (expressed relative to TCDD as induction equivalency factors, IEFs) and (2) relative sensitivity of each species to EROD induction by each compound. Three methods for estimating potency were compared. These were: (1) the concentration of inducer that produced a half-maximal (EC50) EROD response, (2) the concentration producing a response equivalent to 10% of the maximal response produced by TCDD (ECTCDD 10%), and (3) a slope ratio method. For each method, the rank order in potency was TCDD > or = TCDF > PCB 126 > PCB 81 > PCB 77 > PCB 169 in chicken, pheasant, and turkey hepatocytes. The rank order was similar in duck and herring gull hepatocytes with the following exceptions: TCDF was approximately 2- to 4-fold more potent than TCDD in duck hepatocytes; PCB 169 induced EROD in gulls, but PCB 77 had no measurable effect in this species. PCB 118 was a relatively weak EROD inducer in most species/breeds, but it did not induce EROD in Pekin ducks or gulls. PCB 105 was a weak inducer in White Leghorn chicken and turkey hepatocytes, but it did not induce EROD in other species. The EC50, ECTCDD10% and slope ratio methods for estimating potencies generally gave similar IEFs for compounds that produced a maximal response that was at least 60% of the maximal response produced by TCDD. For compounds that caused a response that was 50% or lower than that produced by TCDD, EC50-based IEFs were greater (10- to 100-fold) than ECTCDD10%-based IEFs or slope-ratio-based IEFs. Among species, the rank order in sensitivity to EROD induction was chicken > pheasant > turkey > or = duck > or = herring gull. The relative sensitivity of avian hepatocyte cultures to EROD induction by PCB 77 was similar to the relative sensitivity of these species (reported elsewhere) to lethality after in ovo injection of PCB 77. Chicken hepatocyte cultures were 5-10 times more sensitive to EROD induction by TCDD than were pheasant hepatocyte cultures, which is identical to the difference in sensitivity of these species to the lethal effect of TCDD after in ovo injection. Measuring the sensitivity of hepatocyte cultures to EROD induction might be useful for estimating the sensitivity of avian species (including rare or endangered species, where it is impossible to conduct in vivo studies) to the embryotoxic effects of TCDD, non-ortho substituted PCBs, and other aryl hydrocarbon receptor agonists.

Developmental toxicity study in rats exposed dermally to clarified slurry oil for a limited period of gestation

Clarified slurry oil (CSO, CAS number 64741-62-4), a refinery stream produced by processing crude oil, is a developmental toxicant when administered dermally throughout gestation to pregnant rats. The manifestations of developmental toxicity observed included embryolethality and growth retardation; evidence of teratogenicity was limited, and not conclusive. The present study was undertaken to further explore the teratogenic potential of CSO. In an attempt to limit embryolethality and thereby promote detection of terata, CSO was administered once daily for a limited period of gestation [gestation days (GD) 9-12], via dermal application, to pregnant Sprague-Dawley rats at doses of 0, 10, 100, and 1000 mg/kg. All animals were sacrificed on GD 20. Detailed examination of the dams was performed. Due to the screening nature of this investigation, fetal evaluations were limited to body weight measurements, external examinations, and evaluation of select visceral endpoints. In the dams exposed to CSO, significant decreases in body weight [absolute and gain (GD 9-13, GD 0-20)] and in the amount of food consumed were observed at 100 and 1000 mg/kg. Additional evidence of maternal toxicity observed at 1000 mg/kg included decreased absolute and relative thymus weights, increased absolute and relative liver weights, and aberrant serum chemistry. Ingestion of the test material was evident at the high dose. Developmental toxicity was observed at 1000 mg/kg and included increased embryolethality, decreased body weight, and anomalous development (cleft palate, brachydactyly, edema). Although a low incidence of abnormal fetal development was observed at 100 mg/kg, it was not conclusive that the alterations were due to CSO exposure. It is likely that three to seven-ring polycyclic aromatic compounds present in CSO were responsible for the toxic effects observed.

Bacterial and human cell mutagenicity and mouse lung tumorigenicity of the oxygenated polynuclear aromatic hydrocarbon phenalenone

Phenalenone (perinaphthenone) is a major oxygenated polynuclear aromatic hydrocarbon (oxy-PAH) atmospheric pollutant formed from the combustion of fossil fuels. Mutagenicity of phenalenone was measured in quantitative forward mutation assays with Salmonella typhimurium TM677 and metabolically competent human B-lymphoblastoid cell lines (MCL-5 and h1A1v2 cells), and its tumorigenicity was also assessed in a newborn mouse assay. Phenalenone was mutagenic in Salmonella in the presence of rat liver postmitochondrial supernatant (PMS) at a minimum detectable mutagen concentration (MDMC) of 12 micrograms/ml, but was not mutagenic in the absence of PMS at concentrations up to 100 micrograms/ ml. Phenalenone was not significantly mutagenic in either human cell line after 28 hr treatment, although mutant fractions were increased by nearly fivefold in h1A1v2 cells (at the tk locus) exposed at 30 micrograms/ml. However, after 72 hr treatment, phenalenone was mutagenic at the hprt locus in h1A1v2 cells with an MDMC of 3 micrograms/ml. Phenalenone was also tumorigenic in male BLU:Ha mice with a lung tumor incidence of 33% 6 months after injection with 4.2 mg phenalenone, the highest dose tested. Lung tumor multiplicity in this treatment group was 0.5 tumor/mouse. No increase in lung tumors in female mice was observed. Indices of lung tumor incidence (ED50) and multiplicity (TM1.0) for male mice were 29.3 and 34.9 mumol, respectively. These data suggest that phenalenone does not contribute significantly to the mutagenicity or carcinogenicity of combustion emission extracts.

Developmental toxicity of clarified slurry oil, syntower bottoms, and distillate aromatic extract administered as a single oral dose to pregnant rats

Clarified slurry oil (CSO), syntower bottoms (STB), and distillate aromatic extract (DAE) are refinery streams produced by processing crude oil. Each of these refinery streams is rich in both hydrocarbons having carbon numbers of C20 or greater and polycyclic aromatic compounds. Available data indicate that some refinery streams are developmentally toxic (manifested primarily as increased embryolethality and growth retardation) by the dermal route of exposure. However, there is no conclusive evidence for their being teratogenic. The present studies were designed to further explore the suspected teratogenic potency of refinery streams while at the same time limiting embryolethality. To profile teratogenic effects as a function of gestation day, pregnant rats received a single oral dose (2000 mg/kg) of CSO, STB, or DAE on one of gestation days (GD) 11-14; DAE and STB were also administered on GD 15. To profile effects as a dose response function, rats received a single oral dose of CSO, DAE, or STB on GD 12 at 125, 500, and 2000 mg/kg. Control animals were similarly treated but were administered tap water. On GD 20, dams were necropsied and the fetuses evaluated for normal development. In general, evidence of maternal toxicity (i.e., decreased body weight gain, decreased thymus weight) was observed at doses greater than or equal to 500 mg/kg. For each refinery stream tested, the incidence of resorption was greatest on GD 11. A common pattern of fetal malformations was observed for all of the refinery streams tested and included cleft palate, diaphragmatic hernia, and paw and tail defects. The incidence and type of malformation observed were influenced by the gestation day of exposure. The incidences of external and skeletal malformations were greatest on GD 11 and 12 for fetuses exposed to CSO; on GD 13 and 14, the incidence of malformation was comparable for CSO- and STB-exposed fetuses. The incidence of visceral anomalies was greatest on GD 11-13 for fetuses exposed to CSO and STB; on Gestation D 14, the incidence was comparable for each of the refinery streams tested. In general, the ability to produce adverse effects on development was greatest for CSO and least for DAE. Effects produced by STB were comparable to or less severe than those observed for CSO.

Mutation spectra of chemical fractions of a complex mixture: role of nitroarenes in the mutagenic specificity of municipal waste incinerator emissions

Using an ion-exchange procedure coupled to a microsuspension Salmonella assay, we fractionated the dichloromethane-extractable particulate organics emitted by a municipal waste incinerator. Most (80-95%) of the mutagenic activity resided in the neutral/base fraction; however, the polar neutral fraction accounted for 12% of the direct-acting mutagenic activity. The mutagenic potencies of the whole extract and the various fractions were 4-15 times greater in the absence than in the presence of S9. Results with strains deficient in classical nitroreductase (TA98NR) and transacetylase (TA98/1,8-DNP6) indicated that a majority of the direct-acting mutagenicity was due to nitroarenes. This was confirmed by bioassay-directed subfractionation of the neutral/base faction by a cyanopropyl/HPLC method. The mutations in -3,000 revertants (approximately 400 each induced in TA98 by the whole extract, the neutral/base and polar neutral fractions from the ion-exchange column and 3 of the neural/base subfractions from the HPLC column; along with 200 revertants each induced by the model nitroarene 1-nitropyrene (1NP) in strains TA98, TA1538 and TA100) were analyzed by probe hybridization and PCR/DNA sequence analysis. The results indicated that nitroarenes such as 1NP that eluted in the neutral/base fraction accounted for at least 50% of the direct-acting mutagenicity and induced only a hotspot 2-base deletion in the sequence (CG)4 in TA98. In contrast, most of the complex frameshifts (a frameshift with a flanking base substitution) induced by the whole extract were induced by nitroarenes other than 1NP that were activated by transacetylation and that eluted in the polar neutral fraction. This study (1) identifies nitroarenes as an important contributor to the mutagenic activity of the emissions from municipal waste incinerators; (2) confirms our previous conclusion that the mutation spectrum of a complex mixture reflects the dominance of particular classes of chemical mutagens within the mixture; and (3) demonstrates the possibility of isolating certain chemical fractions of a complex mixture that induce certain classes of mutations produced by the whole, unfractionated mixture.

A rapid and simple method for the analysis of 1-hydroxypyrene glucuronide: a potential biomarker for polycyclic aromatic hydrocarbon exposure

The present study describes a simple method of analyzing metabolites of pyrene in urine. This method is capable of detecting the glucuronic acid and sulfate conjugates of pyrene as well as free 1-hydroxypyrene in a single analysis. In comparison to other analytical methods for detecting pyrene metabolites, this new method does not require an overnight enzymatic hydrolysis step and is much more rapid method of analysis. The newly developed procedure involves solid phase extraction of pyrene metabolites followed by separation using HPLC with a phenyl modified reverse phase column and an acidic buffer and acetonitrile gradient elution system. Metabolites were detected using a fluorescence detector with wavelength conditions optimized for each metabolite. This method resulted in baseline separation of the glucuronic acid (1-OH P-GlcUA) and sulfate conjugate (1-OH P-Sul) of 1-hydroxypyrene and free 1-hydroxypyrene (1-OH P). The potential of this method for use in monitoring human exposure to mixtures of PAHs was evaluated by analyzing urine obtained from five individuals working in a coal gasification plant. 1-OH P-GlcUA was detected as the major metabolite in the urine of all the five workers. This metabolite accounted for 80-100% of the total pyrene metabolites excreted in urine. 1-OH P-GlcUA levels ranged from 0.31-0.94 microgram/g creatinine. Low levels of the sulfate conjugate (0.002-0.06 microgram/g creatinine) were detected in four of the samples while free 1-hydroxypyrene (0.07-0.2 microgram/g creatinine) was detected in two of the five urine samples. Urine from occupationally exposed workers was also analyzed for 1-hydroxypyrene following enzymatic hydrolysis using the standard approach. Levels of 1-hydroxypyrene ranged from 0.51-1.17 micrograms/g creatinine. Comparison of the fluorescence intensities of 1-OH P-GlcUA and 1-OH P-Sul to 1-hydroxypyrene demonstrated that the glucuronide conjugate is 3-fold more fluorescent and the sulfate conjugate is 4-fold more fluorescent than 1-hydroxypyrene. These results indicate that conjugates of pyrene, specifically, 1-OH P-GlcUA can potentially be used as a more sensitive biomarker of exposure to PAHs.

Human exposure and dosimetry of polycyclic aromatic hydrocarbons in urine from Xuan Wei, China with high lung cancer mortality associated with exposure to unvented coal smoke

The lung cancer mortality rate in Xuan Wei (XW) county, China, is 5-fold the national average of China; the rate for women is the highest in China. Xuan Wei residents have been exposed to unvented coal or wood smoke during cooking or heating in homes. This study investigated indoor air exposure and dosimetry of polycyclic aromatic hydrocarbons (PAHs) in XW residents using smoky coal. Indoor air particles collected during cooking in four XW homes using smoky coal were analyzed for PAHs by GC/MS. Urine samples from 16 XW non-smoking women and six XW smoking men, eight Kunming non-smoking controls and four non-smoking Chinese American controls were analyzed for PAHs and hydroxy-PAHs by GC/MS. The results showed that XW residents were exposed to PAHs at occupational levels. The potent carcinogen, dibenzo[a,l] pyrene (4.9 +/- 1.3 micrograms/m3) was found in the indoor air of the XW homes. The levels of urinary hydroxy-PAH were higher than those of the parent compounds in most subjects, indicating that most PAHs were metabolized. In urine, the mean levels of 9-hydroxy BaP (BaP) and BaP are 1.5 +/- 0.5 mumol/mol creatinine and 0.5 +/- 0.3 microns/mol for XW men, 1.9 +/- 0.9 microns/mol and 0.5 +/- 0.3 microns/mol for XW women. In general, the levels of PAH metabolites in urine were higher in the XW residents than in Kunming and Chinese American controls; however only the concentrations of 9-hydroxy BaP in XW women showed statistically significant difference from the Kunming controls (P < 0.05 by ranking test). The mean levels of 3 methylated-PAHs analyzed were 4.8-fold higher than that of the parent PAHs in XW subjects. This is consistent with previous findings that alkylated PAHs are the major mutagens in the XW indoor air and may be etiologically important in XW lung cancer.

Developmental toxicity study of clarified slurry oil (CSO) in the rat

Pregnant CD rats were exposed dermally to 0.05, 1, 10, 50, and 250 mg/kg/day of Clarified Slurry Oil (CSO) on Days 0-19 of gestation to determine its potential developmental toxicity. Untreated and vehicle controls were included in the study. Day 20 of gestation Caesarean-derived fetuses were examined for gross, external, and visceral or skeletal alterations. Dosages of 1 mg/kg/day and higher significantly decreased maternal body weight, body weight gain, feed consumption, gravid uterine weight, and live litter size and significantly increased resorption rate. These dosages also significantly reduced fetal weights and retarded development of the brain, kidney, thoracic and caudal vertebrae, metacarpals, and hindpaw phalanges in dosage groups with live fetuses (high dosage group dams resorbed all conceptuses). The 50- and 250-mg/kg/day dosage group dams had only placentas and/or dark red viscous fluid in the uterus or vagina and significant body weight loss (associated with resorption). The highest dosage also caused emaciation, slight dehydration, and swollen dark anogenital areas. These results indicate that CSO produces adverse developmental effects at maternally toxic dosages. The maternal and developmental NOAELs (no observed adverse effect levels) were 0.05 mg/kg/day. In a second study, groups of 10 mated female rats were exposed to "pulse" exposures and dosages of 1, 50, or 250 mg/kg/day of CSO applied dermally for 2- or 3-day intervals that spanned the gestation period. All dosages reduced maternal feed consumption and body weight gain during the treatment period. Dosages of 50 and 250 mg/kg/day also produced early resorptions when administered on Days 6 through 8 and 9 through 11 of gestation. However, no increase in fetal alterations occurred, indicating that the effects on embryo-fetal development were due to early death and not to the death of malformed conceptuses.

The CAT-Tox (L) assay: a sensitive and specific measure of stress-induced transcription in transformed human liver cells

Identifying and measuring the molecular mechanisms of toxicity is an important goal in hazard assessment. We have developed an assay in transformed human liver cells to simultaneously measure the transcriptional responses of 14 stress promoter- or response element-chloramphenicol acetyl transferase (CAT) fusion constructs that are stably integrated into the HepG2 cell line. This assay can measure a wide spectrum of stresses, both toxic and nontoxic, such as protein and protein biosynthesis perturbations, DNA damage, heavy metals, and planar aromatic hydrocarbons. We found that each promoter or response element can be induced by one or more of four chemicals that were tested in the assay. These results have been interpreted in light of the current models of action for each compound. The responses of this assay system can distinguish among compounds that are closely related in their structure and have been shown previously to elicit similar biological activities in simple assay systems. We have designated this technique the CAT-Tox (L)iver assay. It measures a broad range of cellular stresses and toxicants at levels that were comparable to or below those of established methods. The induction profiles generated using the CAT-Tox (L) assay can help to elucidate the molecular mechanisms by which chemicals exert their actions on human cells. These profiles can be indicative of both toxic and nontoxic processes that are occurring in the cell. We propose that this cellular stress assay can serve as a screen for a variety of substances at the molecular level.

Induction of cytochrome P450-dependent monooxygenase in serum-free cultured Hep G2 cells

We examined the induction of cytochrome P450-dependent mixed-function monooxygenase (MFO) in the human hepatoma cell line Hep G2 by means of several factors. The MFO activities induced in the cells cultured in medium containing five commercial sera varied significantly, and the activity in the cells cultured in the absence of serum was about twice as high as that in cells supplemented with serum. The activity of ethoxycoumarin O-deethylase was highest 12 hr after adding 3-methylcholanthrene, and it was induced by several polycyclic aromatic hydrocarbons such as benzo(a)anthracene and benzo(a)pyrene, which are usually found in urban air as environmental contaminants. Furthermore, an extract from the total suspended particles collected using a high volume air sampler, which was mutagenic in the Ames assay using Salmonella typhimurium TA98, induced the same enzyme activities in Hep G2 cells. These findings suggest that serum-free culture allows the stable and highly sensitive measurement of induced MFO activity, and that studies of MFO induction by environmental samples using human hepatoma Hep G2 cells should provide helpful information regarding the risk associated with environmental contaminants.

beta-Naphthoflavone-inducible cytochrome P4501A1 activity in liver microsomes of the marine safi fish (Siganus canaliculatus)

The cytochrome P450-dependent metabolism of benzo(a)pyrene and other xenobiotics has been investigated in liver microsomes prepared from a local marine safi fish, Siganus canaliculatus. The safi fish was found to have a well-developed microsomal monooxygenase system consisting of cytochrome P450, cytochrome b5 and NADPH-cytochrome c reductase. The fish microsomal enzyme system was able to metabolize benzo(a)pyrene, 7-ethoxycoumarin and 7-ethoxyresorufin. Male fish were found to exhibit a higher monooxygenase activity than female fish. Treatment of fish with beta-naphthoflavone was found to induce (2- to 4-fold) the activities of aryl hydrocarbon hydroxylase, ethoxycoumarin O-deethylase and ethoxyresorufin O-deethylase. HPLC analysis of the metabolites produced by incubation of benzo(a)pyrene with the liver microsomal preparation showed a predominant formation of 3-OH and 9-OH benzo(a)pyrene. There was an increased formation of benzo(a)pyrene 7,8-diol and benzo(a)pyrene 7,8,9,10-tetrol in liver microsomes prepared from beta-naphthoflavone-treated fish. Western immunoblot analysis of liver microsomes from beta-naphthoflavone-treated fish using an antibody to rat liver cytochrome P4501A1 (CYP1A1) suggested the presence of an inducible cytochrome P450 enzyme that was comparable with that of rat liver enzyme. Our results suggest that liver microsomes from the safi fish have multiple forms of cytochrome P450 with a specific beta-naphthoflavone-inducible CYP1A1 homologous protein that can metabolize a variety of substrates.

Metabolic requirements for induction of contact hypersensitivity to immunotoxic polyaromatic hydrocarbons

Experiments were performed to define the metabolic requirements for induction of contact hypersensitivity to polyaromatic hydrocarbons (PAHs), environmental xenobiotics that are both immunotoxic and carcinogenic. Evidence that conversion of the parent compound to a reactive metabolite was necessary for the development of contact hypersensitivity included the fact 1) that contact hypersensitivity to the polyaromatic hydrocarbon dimethylbenz(a)anthracene (DMBA) only occurred in strains of mice that could metabolize the compound, 2) that among the PAHs, only those that could induce aryl hydrocarbon hydroxylase, the rate-limiting enzyme in the PAH metabolic pathway, were immunogenic, and 3) that inhibitors of PAH metabolism reduced DMBA contact hypersensitivity. Cells from the XS52 Langerhans cell-like dendritic cell line were able to metabolize the PAH benzo(a)pyrene to its diol, quinone, and phenol metabolites. GM-CSF augmented benzo(a)pyrene metabolism in XS52 cells. Finally, in vivo depletion of CD8+, but not CD4+, T cell populations inhibited contact hypersensitivity to DMBA. The implications of these experiments are that at least for some contact allergens, the metabolic status of the host is a key determinant of individual susceptibility to the development of allergic contact dermatitis, and the metabolic pathway of an individual hapten may have ramifications for the T cell subpopulation-CD4 or CD8-that is activated.

Mutagenicity of stable dust and drinking water on swine and cattle farms

Single pilot examinations of mutagenicity of stable dust and drinking water were made on three swine farms (D., M., T.) and one cattle farm (N.) in the district of Hodonín in summer 1994. The mutagenicity was examined by the Ames test using the indicator strains Salmonella typhimurium TA 98 and TA 100 with (+S9) or without (-S9) metabolic activation. At the same time the contents of selected pesticides (PES) and polychlorinated biphenyls (PCB) in stable dust and drinking water and that of polycyclic aromatic hydrocarbons in stable dust were determined. Increased mutagenicity was demonstrated in drinking water (strain TA 98 with metabolic activation; index Rt/Rk 3.6-7.7) and stable dust (strain TA 100 with metabolic activation; index Rt/Rk 2.2) collected on the swine farm M. High contents of PAH (8.246 mg/kg) and PCB (0.263 mg/kg) were also found in the dust samples collected on this farm. Only drinking water showed mutagenic activity (strain TA 98 without metabolic activation; index Rt/Rk 2.6) on the swine farm D. On both the farms, the number of revertants was dose-dependent. Increased content of PAH (2.553 mg/kg) was also demonstrated on the dust samples collected on the farm D. No significant increase (twofold or higher when compared with negative controls) of mutagenic activity of stable dust or drinking water was demonstrable on the swine farm T. and the cattle farm N. Substances responsible for the mutagenicity of drinking water on the farms D. and M. have not yet been identified. Anyway, the increase of mutagenicity of stable dust and drinking water should be taken as a warning that mutagens that can jeopardise animal and human health have penetrated into the stable environment.

Genotoxicity of sediment extracts obtained in the vicinity of a creosote-treated wharf to rainbow trout hepatocytes

Genotoxicity and cytotoxicity were evaluated in rainbow trout hepatocytes exposed to sediment extracts obtained in the vicinity of a creosote-treated wharf. Sediment cores were collected at the intertidal and subtidal sections of the wharf at distances of 1, 5, 40 and 50 m. Moreover, subsamples were also taken at different depths of the cores ranging from 2 to 10 cm below the sediment/water interface. Sediment samples were air-dried and extracted in dichloromethane followed with an exchange into dimethylsulfoxide (DMSO). Rainbow trout hepatocytes were exposed for 24 h at 15 degrees C to several concentrations of the sediment extract. Afterwards, the cells were collected, and cell viability was assayed along with genotoxicity using the nick translation and the alkaline precipitation assays. Results showed that the wharf contained high concentration of polycyclic aromatic hydrocarbons (PAHs), displayed genotoxicity and cytotoxicity to hepatocytes. In addition, PAHs, cytotoxicity and sometimes genotoxicity were detected in all sediment samples and tended to decrease with distance. Chemical contamination and (geno)toxic effects were greater in sediment extracts from the intertidal section than from the subtidal section. However, no evident change in chemical or toxicological characteristics was noted between samples obtained at different depths. Spearman rank-correlation analysis revealed some trends between levels of some PAHs and (geno)toxicity in hepatocytes exposed to sediment extracts.

Levels of pollutants and their metabolites: exposures to organic substances

The measurement of levels of organic pollutants and/or their metabolites in body tissues or fluids are specific markers of internal dose and, provided that the pharmacokinetic properties of the compounds in question are known, these levels may also be used as predictors of effects. Although historical data still remain to be very useful in environmental studies, more reliable exposure measures than combination of environmental levels and such estimators as residential history, job titles, life-style habits, individual perceptions, etc., are highly desirable. This has been clearly demonstrated in studies with 2,3,7,8-tetrachlorndibenzo-p-dioxin (TCDD), where more recent measurements of serum concentrations in persons earlier classified as belonging to exposed groups have indicated that severe misclassifications may have occurred in previously epidemiological studies. This also demonstrates that, in retrospective studies, levels of persistent organic compounds are useful as markers of exposure, as their tissue levels mainly reflect previous exposures. However, most organic compounds are readily metabolized and excreted from the human body, and in many instances it will not be possible with current methodology and instrumentation to detect transient organic pollutants at low levels in the blood. In most cases, the use of urine samples offers a better opportunity to provide samples containing detectable levels. Therefore, the measurement of non-persistent organic substances and/or their metabolites may find potential use in prospective environmental health studies, but the predictive value highly depends on proper timing and frequency of sampling according to their toxicokinetic behaviour. A few examples on the use of organic compounds and/or metabolites as biomarkers are given, e.g., polychlorinated dibenzo-p-dioxins (PCDDs) and dibenzofurans (PCDFs), polychlorinated biphenyls (PCBs), polybrominated biphenyls (PBBs), ochratoxin A, polycyclic aromatic hydrocarbons (PAHs) and cooked food mutagens.

Biotransformation of benzo[a]pyrene and other polycyclic aromatic hydrocarbons and heterocyclic analogs by several green algae and other algal species under gold and white light

This laboratory has shown that the metabolism of benzo[a]pyrene (BaP), a carcinogenic polycyclic aromatic hydrocarbon (PAH), by a freshwater green alga, Selenastrum capricornutum, under gold light proceeds through a dioxygenase pathway with subsequent conjugation and excretion. This study was undertaken to determine: (1) the effects of different light sources on the enzymatic or photochemical processes involved in the biotransformation of BaP over a dose range of 5-1200 mg/l; (2) the phototoxicity of carcinogenic PAHs and mutagenic quinones to a green alga; (3) the ability of other algal systems to metabolize BaP. Cultures were exposed to different doses of BaP for 2 days at 23 degrees C under gold, white or UV-A fluorescent light on a diurnal cycle of 16 h light, 8 h dark. Under gold light, metabolites of BaP produced by Selenastrum capricornutum were the dihydrodiols of which the 11,12-dihydrodiol was the major metabolite. Under white light, at low doses, the major metabolite was the 9,10-dihydrodiol. With increasing dose, the ratio of dihydrodiols to quinones decreased to less than two. With increasing light energy output, from gold to white to UV-A in the PAH absorbing region, BaP quinone production increased. Of other carcinogenic PAHs studied, only 7H-dibenz[c,g]carbazole was as phototoxic as BaP while 7,12-dimethylbenz[a]anthracene, dibenz[a,j]acridine and non-carcinogenic PAHs, anthracene and pyrene, were not phototoxic. The 3,6-quinone of BaP was found to be highly phototoxic while quinones that included menadione, danthron, phenanthrene-quinone and hydroquinone were not. The data suggest that the phototoxicity of BaP is due to photochemical production of quinones; the 3,6-quinone of BaP is phototoxic and is probably the result of the production of short lived cyclic reactive intermediates by the interaction of light with the quinone. Lastly, only the green algae, Selenastrum capricornutum, Scenedesmus acutus and Ankistrodesmus braunii almost completely metabolized BaP to dihydrodiols. The green alga Chlamydomonas reinhardtii, the yellow alga Ochromonas malhamensis, the blue green algae Anabaena flosaquae and euglenoid Euglena gracilis did not metabolize BaP to any extent. The data indicate that algae are important in their ability to degrade PAHs but the degradation is dependent on the dose of light energy emitted and absorbed, the dose of PAHs to which the algae are exposed, the phototoxicity of PAHs and their metabolite(s) and the species and strain of algae involved. All of these factors will be important in assessing the degradation and detoxification pathways of recalcitrant PAHs by algae.

Inhibition of sarcoplasmic/endoplasmic reticulum calcium ATPases (SERCA) by polycyclic aromatic hydrocarbons in HPB-ALL human T cells and other tissues

Polycyclic aromatic hydrocarbons (PAHs) are immunosuppressive chemicals found in the environment that have been shown to disrupt intracellular Ca2+ homeostasis and Ca(2+)-dependent signaling in human and murine lymphocytes. Many PAHs produce a rapid and sustained increase in intracellular free Ca2+ in lymphocytes. The mechanism of persistent Ca2+ perturbation remains undefined. In the present studies, ATP-dependent 44Ca2+ uptake into vesicles prepared from a 15,000g supernatant of HPB-ALL human T cell lysates was significantly inhibited by 0.1, 1, and 10 microM concentrations of the immunotoxic PAHs 7,12-dimethylbenz[a]anthracene (DMBA), benzo[a]pyrene (BAP), benz[a]anthracene, and 9,10-dimethylanthracene, but not by the less immunotoxic compounds anthracene (ANT) and benzo[e]pyrene (BEP). Ca(2+)-ATPase catalytic activity was determined by quantitating hydrolysis of ATP in the presence or absence of PAHs, with known ATPase inhibitors included as controls. Formation of inorganic phosphate was significantly decreased (> 65% of control at 10 microM) by DMBA and BAP, whereas ANT and BEP caused only a slight reduction in activity (10% of control at 10 microM). Anthracene partially reversed the inhibitory effect of DMBA and BAP on ATP hydrolysis when agents were coincubated. Both DMBA and BAP, but not ANT and BEP, inhibited the activity of all known SERCA-type Ca(2+)-ATPases, while not affecting either Na+, K(+)-ATPase activity or plasma membrane Ca(2+)-ATPase activities. These results demonstrate that immunotoxic and carcinogenic polycyclic aromatic hydrocarbons have a thapsigargin-like effect in human lymphocytes and SERCA-containing tissues from various species. Inhibition of SERCA activity may play an important role in altered Ca2+ homeostasis in lymphocytes and other tissues.

Role of alterations in Ca(2+)-associated signaling pathways in the immunotoxicity of polycyclic aromatic hydrocarbons

Polycyclic aromatic hydrocarbons (PAHs) are an important class of environmental pollutants that are known to be carcinogenic and immunotoxic. The effects of PAHs on the immune system of various animals and models have been studied for at least 30 yr. Despite these efforts, the mechanism or mechanisms by which PAHs exert their effects on the immune system are still largely unknown. During recent years, the molecular events associated with lymphocyte activation and receptor-mediated signaling have become increasingly clear. Substantial progress has been made in understanding the molecular and cellular bases for toxicant-induced immune cell injury. Understanding mechanisms of drug or chemical effects on the immune system is an important area of research in the field of immunotoxicology, and indeed in all fields of toxicology. Mechanistic toxicology plays an important role in risk assessment and extrapolation of potential human health effects. In this review, we have summarized recent evidence that has examined the effects of PAHs on the immune system of animals and humans. In particular, we have focused on the effects of PAHs on cell signaling in lymphoid cells and have examined the hypothesis that PAHs alter lymphocyte activation via calcium-dependent mechanisms. Previously published reports are discussed, and new data obtained with murine B cells and cell lines are presented demonstrating the relationship between alterations in intracellular calcium and immune dysregulation. These data demonstrate a strong association between PAH-induced alterations in B- and T-lymphocyte activation and changes in calcium homeostasis.

Mutagenicity and contents of polycyclic aromatic hydrocarbons in new high-viscosity naphthenic oils and used and recycled mineral oils

Mutagenic activity on the Ames test was evaluated in 15 samples of naphthenic high-viscosity mineral oils and 12 samples of used lubricants (recovered and pooled) and their recycled products. Bacterial mutagenesis was assayed using both the standard technique and Blackburn's modification. The contents of polycyclic aromatic hydrocarbons (PAH) was also evaluated, as polynuclear aromatic fraction (PAF) and total PAH, determined respectively with the semi-quantitative dimethylsulphoxide-refractive index method and the Grimmer method. Only four samples (three acid-treated naphthenic oils and one recycled fraction of a used oil) showed mutagenic activity higher than 6 revertants/mg of oil, considered by Blackburn and coworkers as indicating a potential carcinogenic risk for these compounds. Limited mutagenicity was found in all used and recycled oils, but also in samples of acid- or solvent-treated oils. No hydrogen-treated naphthenic oils turned out to have any mutagenic activity. PAF contents of oils were closely correlated with those of total PAH (n = 15, r = 0.83; n = 12, r = 0.91; p < 0.01 for both naphthenic and used/recycled oils respectively). No recycled oil had high PAF contents. Eleven samples had PAF contents higher than 3%, the arbitrary danger threshold suggested by the CONCAWE (1988). Of these 11 samples, the majority were acid-treated products, although there was one hydrogen-treated oil and one used and recycled oil. No mutagenic activity could be demonstrated in almost half the oils with PAF > 3%. In this study, the presence of mutagens was not correlated wither with PAF or with total or mutagenic PAH. The difficulty of predicting the mutagenicity of mineral oils is stressed. Most naphthenic and some recycled oils clearly have components which inhibit the metabolizing system in the bacterial mutagenesis test, with consequent possible false negative results.

[Risk for the Rostock water supply from the Warnov river by an old deposit at Schwann?]

Accidents of the city gasworks in the end of the fifties at Schwaan, a small town south of Rostock, resulted in an emission of tar and waste water into the river Warnow, from which the city of Rostock is supplied with drinking water about 20 km downstream. The tar contaminated river sediment (old deposit) covering an area of about 200 m2 has a high pollutant inventory: Steam-distillable phenolic compounds 407 mg/kg in the fresh sediment, polycyclic aromatic hydrocarbons (PAH) 400 to 1100 micrograms/l in the aqueous eluate. The mutagenic potential was detected by the AMES-test. As shown by PAH determinations there were no other pollutant sources in the catchment area, in the tributaries or on other places of the river. The mean PAH concentrations of the river Warnow and his tributaries during 1991 to 1994 were found to be in the range lower than 10 ng/l. Further investigations showed a continuous emission of PAH from the tar laugh in small amounts. An additional emission of pollutants (PAH) and their transportation in the river is expected in the case of sediment disturbances. This emission and their possible consequences are difficult to estimate, even though the seston and the humic substances content of the river seems to reduce the PAH risk. Concluding from our results the probability is very low that pollutants were transported downstream to Rostock and pass the water works but may not totally be excluded. Nevertheless from the viewpoint of care a removal of the old deposit is necessary.

Amphibian micronucleus test in vivo: evaluation of the genotoxicity of some major polycyclic aromatic hydrocarbons found in a crude oil

The micronucleus test using erythrocytes of Pleurodeles waltl larvae (Amphibia, Salamandridae) was used to detect the possible genotoxicity of four polycyclic aromatic hydrocarbons (naphthalene, anthracene, phenanthrene and benzo[a]pyrene), which represent a major fraction of crude oil. Larvae were reared in water containing the test compound and the levels of micronucleated red blood cells were compared with those found in larvae reared in control water. The results are compared with published data from other tests used to evaluate the clastogenic or mutagenic properties of compounds. The results obtained confirm that benzo[a]pyrene has a strong genotoxic potential, whereas the genotoxicity of naphthalene is weak; in contrast, anthracene and phenanthrene gave a negative response.

Biological and environmental monitoring of exposure to airborne benzene and other aromatic hydrocarbons in Milan traffic wardens

Environmental and biological monitoring of airborne aromatic hydrocarbons has been performed in 20 policemen working as traffic wardens exposed to motor vehicle exhausts and in 19 peers employed as clerks. Airborne benzene, toluene, ethylbenzene and xylene concentrations, measured during the workshift, resulted in significantly higher outdoor than indoor concentrations (benzene and related aromatic hydrocarbons mean values, respectively of 53 and 350 micrograms/m3 vs. 29 and 180 micrograms/m3). Blood benzene, toluene, ethylbenzene and xylene concentrations did not differ significantly between indoor and outdoor workers; no differences were found between values obtained at the beginning (07:30 h) and the end of shift (00:30) in either group. Blood hydrocarbon concentrations seem to reflect airborne pollution, whilst the blood benzene concentration determined after the workshift poorly reflects airborne benzene morning peaks. Endshift blood benzene mean concentration in smokers (462 ng/l, n = 9) differs significantly from non-smokers (292 ng/l, n = 39).

Comparative investigations among meteorological conditions, air chemical-physical pollutants and airborne particulate mutagenicity: a long-term study (1990-1994) from a northern Italian town

The findings of a continuos monitoring (Apr90-Mar94) on urban air quality of a Po Valley town are reported. Chemical-physical and genotoxicity data were detected. The results show the presence of mutagenic agents during the whole investigated period. Short term mutagenesis tests together with chemical-physical parameters analysis are able to better assess air quality and genotoxic risk for the population.

The use of in vitro DNA adduct formation to estimate the genotoxicity of residues at contaminated sites

Genotoxic carcinogens such as polycyclic aromatic hydrocarbons (PAHs) covalently bind to the bases in DNA to form adducts. The formation of DNA adducts is significant with respect to chemical carcinogenesis. Many contaminated sites contain quantities of carcinogens such as PAHs, and the evaluation of the genotoxicity of these soils has important implications for human risk assessment. DNA adducts can be formed using an in vitro system incorporating extracts from contaminated soils. The 32P-postlabelling assay is a sensitive technique for the detection of DNA adducts from complex mixtures of environmental carcinogens. These techniques have been used to form and detect DNA adducts using soils from a number of coal gasworks sites. The results show that the extent of adduct formation depends partially on the petroleum hydrocarbon content of samples, but also on other undetermined factors related to composition. While environmental weathering has been shown to effect the PAH composition of samples, this is not an important factor in controlling the genotoxicity of samples as estimated by DNA adduct formation.

Biochemical screening of highly toxic aromatic contaminants in river sediment and comparison of sensitivity of biological model systems

Fractions containing polycyclic aromatic hydrocarbons (PAHs), polychlorinated dibenzo-p-dioxins and dibenzofurans (PCDD/Fs) and polychlorinated biphenyls (PCBs) were extracted from river sediments by various extraction methods. The amount of individual pollutants was determined analytically and data compared with biological assays. These were based on the induction of cytochrome P450 1A1 (CYPIA1) after treatment with sediment fractions in two different biological model systems, a mouse hepatoma cell line Hepa-1 and a chick embryo. In the hepatoma cell culture Hepa-1 significant correlations with analytical results were found for fractions containing PCDD/Fs and planar and mono-ortho-chlorinated PCBs. However for PAH fraction an undesirable decrease of P450 1A1 induction was observed in higher concentrations of this fraction. This decrease was not observed in the chick embryo liver microsomes and biological responses towards the PAH fractions correlated with analytical data. Comparative investigations demonstrated that the chicken embryo hepatic microsomes were more sensitive for PAHs, and the hepatoma cell line Hepa-1 for PCDD/Fs and planar and mono-ortho-chlorinated PCBs.

Urinary excretion of mutagens in coke oven workers

The influence of occupational exposure to polycyclic aromatic hydrocarbons (PAHs) on urinary mutagenic activity was assessed in 75 coke oven workers, using a highly sensitive bacterial mutagen technique (extraction with C18 resin and liquid micro-preincubation test on strain TA98 of Salmonella typhimurium in the presence of metabolizing and deconjugating enzymes). Exposure to PAHs was assessed according to the urinary excretion of 1-pyrenol; the main confounding factors were checked by the number of cigarettes smoked per day and the levels of nicotine and its metabolites in urine, or by ascertaining whether recommended dietary restrictions had been followed. Of the 20 urine samples which turned out to be positive (producing at least double the number of spontaneous revertants), 19 (95%) belonged to smokers. Only one non-smoker had obvious urinary mutagenic activity, and was highly exposed occupationally to PAHs (urinary 1-pyrenol of 3.930 mumol/mol of creatinine). Of the five urine samples from subjects who had not followed the recommended diet, two (40%) were clearly mutagenic. Multiple regression analysis (n = 67) showed that the presence of samples positive for urinary mutagenic activity depended only on smoking habits, if this confounding factor was assessed according to the number of cigarettes smoked per day, while the significant influence of exposure to PAH could be shown when the confounding factor was objectively estimated according to the urinary levels of nicotine and its metabolites. Assessment of the mutagenic potency of urinary extracts (net revertants/mmol creatinine) confirmed the strong influence of smoking habits on urinary mutagenic activity (all smokers 2156 +/- 2691 versus non-smokers 939 +/- 947 net revertants/mmol creatinine; Mann-Whitney test: P < 0.01). In smokers highly exposed to PAHs, greater excretion of mutagens with respect to low-exposure smokers was revealed (3548 +/- 4009 versus 1552 +/- 1227 net revertants/mmol creatinine; Mann-Whitney test: P < 0.01). Multiple regression analysis showed that the mutagenic potency of urinary extracts of coke oven workers depended on exposure to PAHs, tobacco smoking habits, and consumption of fried, grilled or barbecued meat. Increased urinary mutagenic activity strengthens epidemiological evidence of the increased risk of renal and urinary tract tumours in these workers. The presence of mutagenic metabolites in urine as a result of occupational exposure to PAH may be demonstrated only by using highly sensitive techniques for assessing urinary mutagenic activity in studies which include careful checking of the main confounding factors.

The effect of fuel composition on the mutagenicity of diesel engine exhaust

The effect of fuel composition on the mutagenicity of diesel engine emission was investigated. To this end, a fuel matrix comprising fuels with different contents of aromatic and naphthenic compounds was used. Extracts of the organic phase of raw exhausts obtained with different fuels were tested for mutagenicity in bacterial reversion assays. The results obtained demonstrate that the mutagenicity of diesel exhaust is largely dependent on the aromatic content of the fuel. In fact, mutagenicity was greatly reduced when the aromatic content of the fuel was lowered by hydrogen treatment. Conversely, mutagenicity was enhanced when the fuel was enriched with fractions of di- or triaromatic compounds. The addition of di- and trinaphthenic compounds only produced borderline mutagenicity. No clear relationship was observed between sulfur content of the fuel and mutagenicity of the exhaust. Assays in bacterial strains with different sensitivity to nitroaromatic compounds suggest a low contribution of the highly mutagenic dinitropyrenes to the responses observed, and a relatively greater contribution of 1-nitropyrene or other nitroaromatics processed by the same bacterial nitroreductase.

Molecular mechanics explanation for the stereochemical and shape selectivity of B-DNA for "bay-region" carcinogens

The equilibrium structures of 20 intercalated physical complexes of "bay-region" triol carbocations of polycyclic aromatic hydrocarbons (PAHs) with B-DNA are obtained by AMBER molecular modeling. The complexes with highly potent carcinogens are found (i) to undergo only minor conformational changes upon complexation, (ii) to be stabilized by hydrogen bonds between two hydroxyl groups of the triol carbocations and N3 atoms of the adjacent guanine residues, and (iii) to be "preorganized" for covalent bonding. A new explanation for the absolute stereochemical and shape dependence of carcinogenesis by PAHs is presented. The biologically active conformers of both carcinogenic stereoisomers (anti and syn) of triol carbocations are characterized by a quasi-diaxial orientation of the neighboring hydroxyl groups and fulfill the spatial requirements for hydrogen bonding to the adjacent guanine residues of B-DNA. The striking dependence of potency on the shape of the PAHs is largely caused by repulsion from the C2'-methylene groups of the deoxyribose residues of DNA. This interaction may shift the intercalated triol carbocation, thereby enhancing or reducing the preorganization for covalent bonding. The molecular modeling study is augmented by benchmark ab initio calculations on the bay-region triol carbocation of phenanthrene.

Adenomas induced by polycyclic aromatic hydrocarbons in strain A/J mouse lung correlate with time-integrated DNA adduct levels

The induction of DNA adducts and adenomas in the lungs of strain A/J mice has been investigated following the single i.p. administration of each of the following polycyclic aromatic hydrocarbons (PAH): pyrene, dibenz[a,h]anthracene, benzo[a]pyrene, benzo[b]fluoranthene, 5-methylchrysene, and cyclopenta[c,d]pyrene. DNA adducts were measured by 32P-postlabeling at times between 1 and 21 days following injection, while adenomas were counted at 240 days after treatment. Pyrene did not induce either DNA adducts or lung adenomas at any of the doses examined. Each of the remaining PAH induced both adenomas and DNA adducts in a dose-dependent manner, with dibenz[a,h]anthracene > 5-methylchrysene > cyclopenta[c,d]pyrene > benzo[a]pyrene > benzo[b]fluoranthene. DNA adducts reached maximal levels between 3 and 9 days after injection, followed by a gradual decrease. The time-integrated DNA adduct level (TIDAL) was calculated by numerically integrating the areas under the adduct persistence curves extrapolated to 240 days for each PAH at each dose level. This value represents the effective total molecular dose of PAH that was delivered to the lung DNA over the entire course of tumorigenesis. A strong correlation of lung adenoma induction with the TIDAL values was observed for each PAH. The slopes of the tumors versus TIDAL value relationships were essentially identical for 5-methylchrysene, cyclopenta[cd]pyrene, benzo[a]pyrene, and benzo[b]fluoranthene. The slope of this relationship for dibenz[a,h]anthracene was markedly greater. The essentially identical induction of adenomas as a function of TIDAL values for these PAH suggests that the formation and persistence of DNA adducts determines their carcinogenic potency.

Genotoxic activity of environmentally important polycyclic aromatic hydrocarbons and their nitro derivatives in the wing spot test of Drosophila melanogaster

The genotoxicity of three polycyclic aromatic hydrocarbons (PAHs) and of three of their nitro derivatives was evaluated in the wing Somatic Mutation And Recombination Test (SMART) in Drosophila melanogaster. Two crosses were used, i.e. the standard cross (ST) and the improved high bioactivation cross (HB) which is characterised by an increased sensitivity to the genotoxic effects of promutagens and procarcinogens. Larvae trans-heterozygous for the two recessive wing cell markers multiple wing hairs (mwh) and flare (flr3) were fed with the test compounds for 48 h. The wings of the surviving flies were analysed for the occurrence of single and twin spots. Naphthalene, 1-nitronaphthalene and 1,5-dinitronaphthalene proved to be more genotoxic in the HB cross than in the ST cross. Anthracene showed a clear genotoxic activity only in the HB cross whereas it was negative in the ST cross. 9-Nitroanthracene gave inconsistent results in both crosses. Phenanthrene was negative in the ST cross, but weakly positive in the HB cross. These results demonstrate that the genotoxic activity of these PAHs and their nitro derivatives can be detected with the somatic cells of the wing imaginal discs of larvae with high bioactivation capacity.

Detection of polycyclic aromatic hydrocarbon exposure damage using different methods in laboratory animals

Benzo[a]pyrene, benzo[b]fluoroanthene and dibenzo[a,h]anthracene dissolved in a 1:2 mixture of dimethylsulphoxide (DMSO) and water were administered to two groups of female mice, each group containing 15 mice. The doses were administered orally (via gavage) at the respective rates of 1 and 100 micrograms kg-1 body weight five times per week for a period of 9 weeks. The influence of the polycyclic aromatic hydrocarbons (PAHs) was determined using the following methods: determination of DNA-PAH adducts, of chromosome injuries (micronucleus test), of induction of repair using the unscheduled DNA synthesis (UDS) test, and by examination of the DNA structure after nucleoid sedimentation. All the methods investigated provided evidence of a significant effect resulting from exposure to PAHs on the parameters examined. Following chronic exposure to PAHs, the formation of DNA-PAH adducts and injury to the genetic material, as well as the appearance of micronuclei (micronucleus test), the induction of unscheduled DNA synthesis (UDS test) and mutation of the DNA structure (nucleoid sedimentation), were demonstrated. The described methods therefore provide a means for the detection of genetic damage caused by PAH exposure in humans.